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JPS62244425A - Decomposition of tetranitromethane - Google Patents

Decomposition of tetranitromethane

Info

Publication number
JPS62244425A
JPS62244425A JP62083134A JP8313487A JPS62244425A JP S62244425 A JPS62244425 A JP S62244425A JP 62083134 A JP62083134 A JP 62083134A JP 8313487 A JP8313487 A JP 8313487A JP S62244425 A JPS62244425 A JP S62244425A
Authority
JP
Japan
Prior art keywords
tnm
nitric acid
tetranitromethane
gas
temperature
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP62083134A
Other languages
Japanese (ja)
Inventor
チン,チヤング−ワ
エドモンズ,アントニー・チヤールス・フオスター
エバンス,コリン・マイケル
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
PPG Architectural Coatings Canada Inc
Original Assignee
CIL Inc
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by CIL Inc filed Critical CIL Inc
Publication of JPS62244425A publication Critical patent/JPS62244425A/en
Pending legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07BGENERAL METHODS OF ORGANIC CHEMISTRY; APPARATUS THEREFOR
    • C07B63/00Purification; Separation; Stabilisation; Use of additives
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/40Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by heating to effect chemical change, e.g. pyrolysis
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07BGENERAL METHODS OF ORGANIC CHEMISTRY; APPARATUS THEREFOR
    • C07B43/00Formation or introduction of functional groups containing nitrogen
    • C07B43/02Formation or introduction of functional groups containing nitrogen of nitro or nitroso groups
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/06Explosives, propellants or pyrotechnics, e.g. rocket fuel or napalm
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20Organic substances
    • A62D2101/26Organic substances containing nitrogen or phosphorus
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20Organic substances
    • A62D2101/28Organic substances containing oxygen, sulfur, selenium or tellurium, i.e. chalcogen
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10STECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S149/00Explosive and thermic compositions or charges
    • Y10S149/124Methods for reclaiming or disposing of one or more materials in a composition

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Emergency Management (AREA)
  • General Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Business, Economics & Management (AREA)
  • Health & Medical Sciences (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Control Of El Displays (AREA)
  • Treating Waste Gases (AREA)
  • Crystals, And After-Treatments Of Crystals (AREA)
  • Gyroscopes (AREA)
  • Nitrogen Condensed Heterocyclic Rings (AREA)
  • Pyridine Compounds (AREA)

Abstract

A process for the management of by-product tetranitromethane (TNM) which avoids the hazards of the prior art isolation or extraction procedures. A selected in-plant liquid or vapour stream, or a reactor off-gas stream from nitration or nitric acid oxidation plant, which contains TNM, is heated to effectively pyrolyse the TNM without undue losses of nitric acid values.

Description

【発明の詳細な説明】 本発明は有機物質を硝酸で処理する際に生ずるテトラニ
トロメタンの分解方法に関する。特に本発明は硝酸を使
用する酸化又はニトロ化反応で生ずる危険な副生物を早
期に分離しそして経済的にかつ連続的に分解するための
別個の二次的方法を提供する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for decomposing tetranitromethane produced when organic substances are treated with nitric acid. In particular, the present invention provides a separate, secondary method for the early separation and economical and continuous destruction of hazardous by-products produced in oxidation or nitration reactions using nitric acid.

上記ニトロ化反応及び酸化反応は周知であり、又産業界
で広〈実施されている。これらの方法では、爆薬や医薬
、染料、プラスチック、殺虫剤及び多くの他の商品を製
造するだめの中間体のような価値のある製品が提供され
ている。しかしながら、これらの方法の多くにおいて多
量の危険な副生物、即ちテトラニトロメタン(TNM)
も生じていることは余り知られていない。
The above nitration and oxidation reactions are well known and widely practiced in industry. These processes provide valuable products such as intermediates for manufacturing explosives, pharmaceuticals, dyes, plastics, pesticides, and many other commercial products. However, many of these methods produce large amounts of dangerous by-products, namely tetranitromethane (TNM).
It is not well known that this also occurs.

TNMは2つの理由で危険である。第1の理由はその高
い毒性である。このTNMは皮屑との接触又は蒸気の吸
入によって急速に人体に吸収される。第2の理由はTN
Mは純粋な状態では爆発性ではないが、炭化水素や他の
非極性燃料を容易に溶解し、大きな爆発力と高感度を示
す水と非混和性で重い爆発性の液体を生じることである
TNM is dangerous for two reasons. The first reason is its high toxicity. This TNM is rapidly absorbed by the human body through contact with skin debris or inhalation of the vapors. The second reason is TN
Although M is not explosive in its pure state, it easily dissolves hydrocarbons and other non-polar fuels, producing a heavy explosive liquid that is immiscible with water and exhibits great explosive power and high sensitivity. .

他の方法で副生物として生じるTNMの量は通常は極め
て少量である。しかしながら、窒素化合物含有ヒユー 
ム(ni trogenous fume )及び廃酸
中に存在する残留稙酸を回収及び再濃縮する最近の方法
では、TNMは回収された硝酸中に吸収された状態で反
応器に再循環される。従って、TNMが少量しか生じな
い場合であっても、TNM濃度が徐々にかつ累積的に増
大し、従って、潜在的な危険性が増大する可能性がある
The amount of TNM produced as a by-product in other processes is usually very small. However, nitrogen compound-containing fumes
In current methods of recovering and reconcentrating residual nitric acid present in nitrogenic fume and waste acid, the TNM is recycled to the reactor absorbed in the recovered nitric acid. Therefore, even if only small amounts of TNM are produced, the TNM concentration can gradually and cumulatively increase, thus increasing the potential danger.

製品中KTNMが不純物として存在すると危険であるこ
とは知られている。トリニトロトルエンの場合の栂性効
果は火薬倉Jボの作業員によって認められている。幾つ
かのニトログリセリンをペースとする爆薬については、
安全な貯m時間が短くなることが記録されている。この
ような問題を解決するために、従来から、製品を弱アル
カリ性亜饋酸塩溶液で洗浄することが行われてきた。こ
の処理によってTNMは有毒なトリニトロメタンの亜憾
酸塩として洗液中に抽出される。しかしながら、このよ
うな処PIIは水溶性の製品については不可能である。
It is known that the presence of KTNM as an impurity in products is dangerous. The long-term effect of trinitrotoluene has been recognized by the workers at the gunpowder warehouse Jbo. For some nitroglycerin-based explosives,
It has been recorded that the safe storage time is shortened. In order to solve such problems, products have traditionally been washed with a weakly alkaline athrite solution. This process extracts TNM into the wash liquor as the toxic trinitromethane aphrite. However, such treatment PII is not possible for water-soluble products.

TNMは揮発性の物質である。TNMは、しばしば、該
TNMが生成した反応器から、反応器排出ガス中の蒸気
として逃散する。仁れらのガスは史に窒業酸化物を含み
、又、通常は硝酸蒸気も含有している。このようなガス
状物質を分離し且つ環境汚染を防止するための回収方法
は、空気で希釈したガスを希硝酸で洗浄することからな
る。
TNM is a volatile substance. TNM often escapes from the reactor where it is produced as vapor in the reactor exhaust gas. These gases historically contain nitrous oxides and usually also contain nitric acid vapor. A recovery method for separating such gaseous substances and preventing environmental pollution consists in washing the gas diluted with air with dilute nitric acid.

TNMはこの処理では吸収されず、吸収装置中を通過し
て煙突ガスとして放出される。その結果汚染の危険が生
じ且つTNM中の回収可能な窒素分が浪費されることに
なる。更にTNMは吸収器中の低温の条件下では分離し
た液相として凝縮し、これによって明らかな危険性を生
じる可能性もある。これらのTNMの放出を最小限にし
且つ煙突ガス流からTNMを販売可能な誘導体として抽
出する方法が開発さ、れている。米国特許第4,001
゜373号及び同4,003,977号明細書には、ガ
ス流をアルカリ水溶液で洗浄することによりTNMをト
リニトロメチド塩(trinitromechide 
5alt )として吸収することが記載されている。次
にこの廃坑浄液を酸性化することによりトリニトロメタ
ンを遊離させる。これはTNMに非常に類似した性質を
崩する危険な物質である。上記方法の欠点は多量のアル
カリを使用し、この場合、常に処理ガス中にかなりの量
の二酸化炭素が存在することである。これらの要因とこ
の方法の実施に必要とされる装置の大きさと複雑性との
ために、この方法は広く使用されることができな、かっ
たものと考えられる。
TNM is not absorbed in this process and is passed through the absorber and released as stack gas. This results in a risk of contamination and a waste of the recoverable nitrogen content in the TNM. Moreover, TNM can also condense as a separate liquid phase under the low temperature conditions in the absorber, thereby creating a distinct danger. Methods have been developed to minimize the release of these TNMs and to extract them from stack gas streams as salable derivatives. U.S. Patent No. 4,001
No. 373 and No. 4,003,977 disclose that TNM is treated with trinitromethide salt by washing the gas stream with an aqueous alkaline solution.
It is described that it is absorbed as 5alt). Next, trinitromethane is liberated by acidifying this waste mine cleaning fluid. This is a dangerous substance that destroys properties very similar to TNM. The disadvantage of the above method is that large amounts of alkali are used and in this case considerable amounts of carbon dioxide are always present in the process gas. Because of these factors and the size and complexity of the equipment required to implement this method, it is believed that this method has not been able to be widely used.

化学反応器を中程度或いは低い温度で操作する場合には
、副生物であるTNMは廃酸中に溶解した状態で残留し
得る。回収操作によって、揮発性で且つ親油性のTNM
が高濃度の硝酸中に濃縮され、これが循環される傾向が
ある。米国特許第3.781,374号明細書にはこの
ような硝酸源からTNMを分離する方法が記載されてい
る。硝酸を注意深く蒸留することによって、99%の以
上の硝酸中に30チのTNMを含有する共沸濃縮物に近
い最も揮発性の留分を得ることができる。この留分を分
離し次いで水で希釈し冷却することくよって、希硝酸の
下方にTNMの分離層を得ることができる。このTNM
を分離し次いで水洗することによって、販売可h1弓な
品質のTNMが得られる。
If the chemical reactor is operated at moderate or low temperatures, the by-product TNM may remain dissolved in the waste acid. The recovery operation removes volatile and lipophilic TNM.
is concentrated in high concentrations of nitric acid, which tends to be recycled. U.S. Pat. No. 3,781,374 describes a method for separating TNM from such a nitric acid source. By carefully distilling the nitric acid, it is possible to obtain the most volatile fraction, close to an azeotropic concentrate containing more than 99% of 30 TNM in nitric acid. By separating this fraction, diluting it with water and cooling it, a separate layer of TNM can be obtained below the dilute nitric acid. This TNM
By separating and washing with water, TNM of salable quality is obtained.

同時に生じる希硝酸流は再濃縮し、再循環させ得るが、
これらの操作にかなりの費用を要する。
The simultaneous dilute nitric acid stream can be reconcentrated and recycled;
These operations require considerable expense.

この方法の経済性、TNMに対する低い需要及び純粋な
この物質を取扱う際の危険性によって、上記の方法の広
い利用が阻害されていると思われる。
The economics of this process, the low demand for TNM and the dangers of handling this material in its pure form appear to have inhibited widespread use of the above process.

従って副生物として生じるTNMに伴われる毒性と爆発
の危険性を完全に回避することができるftN便な方法
が要望されている。
Therefore, there is a need for a fN convenient method that can completely avoid the toxicity and explosive risks associated with TNM produced as a by-product.

従って、本発明の1つの目的は、硝酸を使用する方法の
副生物であるTNMの分解を完全にかつ経済的に行う方
法であって、公知の方法の場合の危険性と欠点とを排除
し得る方法を提供することである。
One object of the present invention is therefore a complete and economical process for the decomposition of TNM, a by-product of processes using nitric acid, which eliminates the risks and disadvantages of known processes. The goal is to provide a way to obtain

本発明の別の目的は、価値のあるかつ回収可能な窒素分
を損失すること冷しにTNMを分解する方法を提供する
ことである。これらの窒素分はTNMの分解によって必
然的に生ずる窒素酸化物を含有している。同時に生じる
硝酸の分解によっても最少量の伺加的な窒素酸化物が生
じる。
Another object of the present invention is to provide a method for cold decomposition of TNM without loss of valuable and recoverable nitrogen content. These nitrogen components contain nitrogen oxides inevitably produced by the decomposition of TNM. The simultaneous decomposition of nitric acid also produces minimal amounts of additional nitrogen oxides.

本発明によれば、特に、硝酸蒸気を包含する他のガスの
存在下でTNMを選択的に分解する方法が提供され、該
方法はTNMを含有する混合物を215乃至300″C
,好援しくは220乃至3006C。
In accordance with the present invention, there is provided a method for selectively decomposing TNM in the presence of other gases, including, inter alia, nitric acid vapor, the method comprising heating a mixture containing TNM at 215 to 300"C.
, preferably 220 to 3006C.

最も好ましくけ220乃至250’Cの範囲の温度に加
熱しかつ0.1乃至100秒間、好韮しくは0.5乃至
5秒間この温度に保持することからなる。次に生成物の
混合物を冷却及び別に処理することによって存在してい
る有用な窒素分を回収することができる。
Most preferably it consists of heating to a temperature in the range of 220 to 250'C and holding at this temperature for 0.1 to 100 seconds, preferably 0.5 to 5 seconds. The useful nitrogen content present can then be recovered by cooling and treating the product mixture separately.

TNMは上昇温度ではある時点で分解することは知られ
ている。しかしながら、驚くべきことに、T N Mの
早い時期におけるかつ経済的な分離を実施した場合には
、必然的に存在している本来不安定な硝酸が、TNMを
分解するための苛酷な熱処理においてほとんど分解せず
に残留することが認められた。本発明の経済的な成功は
主としてこの驚くべき知見に基づくものである。それは
窒素酸化物から濃る口酸を再生することは技術的に可能
であるが、高価であるという理由による。この高価であ
るという理由は、その方法が希硝酸として吸収するため
の大きな装置を使用し、次いで再濃縮中に著しい量のエ
ネルギーを使用する必要があることにある。
It is known that TNM decomposes at some point at elevated temperatures. Surprisingly, however, if an early and economical separation of TNM is carried out, the naturally unstable nitric acid that is necessarily present will not survive the harsh heat treatment to decompose the TNM. It was observed that it remained without decomposing. The economic success of the present invention is primarily based on this surprising finding. This is because it is technically possible to regenerate concentrated oral acid from nitrogen oxides, but it is expensive. The reason for this high cost is that the process requires the use of large equipment for absorption as dilute nitric acid and then the use of significant amounts of energy during reconcentration.

次に本発明の実施例を示す。Next, examples of the present invention will be shown.

実施例1 芳香族化合物をニトロ化してプラスチックス中間体を製
造する工業的方法では、ニトロ化媒体として硝酸を使用
する。ニトロ化反応器から流出する生成物混合物は、硝
酸中にプラスチックス中間体が溶解した溶液であり、こ
のf8液は次に落下フィルム式蒸発器に送る。この蒸発
器では大部分の硝酸とTNMが蒸気として上方に除去さ
れる。この蒸気を2段階で凝縮させることにより、より
揮発性の凝縮物として13.5 Kg / hrのTN
M(溶解したNOxとともに)を含有している99チ以
上の硝酸が2.2soKq/hrの割合で得られる。プ
リーチャー(bleacher )中で処理して溶解し
ているNOxの大部分をストリップした後、ストリップ
された凝縮液流は連続蒸留カラムに送った。12Kp/
hrのTNMを含有する44Kg/hrの99%以上の
硝酸からなる最も揮発性の頂上留分を、若干の残留NO
x及び酸素とともにガスとして除去した。このガスと蒸
気流を凝縮させることなしにタンタルチューブからなる
熱分解装置に送入した。この管は外部電気部材によって
加熱されており、そこを通ルカス混合物は250″CK
達した。この管の寸法はガスの滞留時間が1秒になるよ
うに設計されている。この装置内で99%のTNM75
Kf″1i化炭素とNOxに変換され、40%未満の硝
酸が分解した。
Example 1 An industrial process for nitrating aromatic compounds to produce plastics intermediates uses nitric acid as the nitration medium. The product mixture exiting the nitration reactor is a solution of plastics intermediates in nitric acid, and this F8 liquid is then sent to a falling film evaporator. In this evaporator most of the nitric acid and TNM are removed upwards as vapor. By condensing this vapor in two stages, 13.5 Kg/hr of TN is produced as a more volatile condensate.
More than 99 H nitric acid containing M (along with dissolved NOx) is obtained at a rate of 2.2 soKq/hr. After treatment in a bleacher to strip most of the dissolved NOx, the stripped condensate stream was sent to a continuous distillation column. 12Kp/
The most volatile top fraction consisting of over 99% nitric acid at 44 Kg/hr containing hr TNM with some residual NO
It was removed as a gas together with x and oxygen. The gas and vapor streams were passed to a pyrolysis device consisting of tantalum tubes without condensation. This tube is heated by an external electrical element and the cass mixture passes through it to 250"CK
Reached. The dimensions of this tube are such that the gas residence time is 1 second. 99% TNM75 in this device
Kf'' was converted to carbon and NOx, and less than 40% of nitric acid was decomposed.

このガス混合物の全部を希釈空気と混合して廃ガス暇収
塔に送入し、そこで硝酸とNOx (この装置”とニト
ロ化プラントの他の場所からのもの)を希硝酸中に吸収
させた。この塔からの濃度アップした希硝酸は再濃縮に
よって回収し、一方、TNMの分解によって生じた酸化
炭素は大気中に放出させた。
All of this gas mixture was mixed with diluted air and sent to a waste gas recovery tower where nitric acid and NOx (from this unit and elsewhere in the nitration plant) were absorbed into the diluted nitric acid. The concentrated dilute nitric acid from this column was recovered by reconcentration, while the carbon oxide produced by the decomposition of TNM was released into the atmosphere.

実施例2 化学的に耐久性のある塩素化芳香族原料をニトロ化して
除草剤の中間体を製造する装置では、100乃至1】5
℃の濃硝酸と硫酸との混合物を一連の反応器中で使用す
る。この反応器系の排ガスは、60 Kg/ brの塩
素と塩化水素との混合物11重量%、二酸化炭素55%
、−酸化炭素1%、硝11112蒸気25%、水1チ及
びTNM5%からなる。
Example 2 In an apparatus for producing a herbicide intermediate by nitrating a chemically durable chlorinated aromatic raw material, 100 to 1]5
A mixture of concentrated nitric acid and sulfuric acid at 0.degree. C. is used in a series of reactors. The exhaust gas from this reactor system is a mixture of 60 Kg/br of chlorine and hydrogen chloride, 11% by weight, and 55% carbon dioxide.
, - 1% carbon oxide, 25% nitrate 11112 vapor, 1 tsp water and 5% TNM.

このガス混合物を電気的に加熱した石英管からなる熱分
解装置に11有すと、そのガス混合物の温度は一秒間で
250℃に上昇した。この処理によって99%以上のT
NMが分解し、一方、99%の硝酸は未分解のまま残留
した。このガス流を冷却器に通し、且つ次いで吸収液と
して硫酸を使用するガススクラバーに送入して、硝酸の
すべてとNOxを効果的に除去し、残留する塩素、塩化
水素及び二酸化炭素を選択的吸収装置で処理した後、大
気中に放出させた。硫酸中の硝酸とNOx溶むけ次いで
新しいニトロ化酸混合物を製造するために使用される。
When this gas mixture was placed in a pyrolysis device 11 consisting of an electrically heated quartz tube, the temperature of the gas mixture rose to 250° C. in one second. Through this treatment, more than 99% of T
NM was decomposed, while 99% of nitric acid remained undecomposed. This gas stream is passed through a condenser and then into a gas scrubber using sulfuric acid as the absorption liquid to effectively remove all nitric acid and NOx, and selectively remove remaining chlorine, hydrogen chloride, and carbon dioxide. After treatment in an absorption device, it was released into the atmosphere. The nitric acid and NOx in sulfuric acid are then dissolved and used to produce a new nitrated acid mixture.

TNMO熱分解は種々の時期(juncture )で
行うことができることは当業者に自明であるが、加熱と
冷却との必要性が最少になるようにTNMが高濃度であ
る時期に本発明を実施するのが最も有利である。又、同
時に熱分解条件にさらされる硝酸の量を最少限にして、
酸の分解と再生コストによる損失を最少にすることも有
利である。又、熱分解が蒸気又はガス流を吸収装置に送
る前に生起するように調整することが有利である。
It will be apparent to those skilled in the art that TNMO pyrolysis can be carried out at various junctions, but the present invention is practiced at a time when the TNM is at high concentration so that the need for heating and cooling is minimized. is the most advantageous. At the same time, the amount of nitric acid exposed to pyrolysis conditions is minimized.
It is also advantageous to minimize losses due to acid decomposition and regeneration costs. It is also advantageous to arrange for pyrolysis to occur before sending the steam or gas stream to the absorption device.

Claims (1)

【特許請求の範囲】 1、有機物質を硝酸で処理する方法で副生物として生ず
るテトラニトロメタンを分解する方法において、テトラ
ニトロメタン含有留分を少なくとも210℃の温度で加
熱処理してテトラニトロメタンを分解することを特徴と
するテトラニトロメタンの分解方法。 2、テトラニトロメタン含有留分を210乃至300℃
の温度で0.1乃至200秒間加熱する特許請求の範囲
第1項に記載の方法。 3、硝酸で処理する方法がニトロ化である特許請求の範
囲第1項に記載の方法。 4、硝酸で処理する方法が酸化である特許請求の範囲第
1項に記載の方法。 5、テトラニトロメタン含有留分が排出ガス及び蒸気か
らなる特許請求の範囲第1項に記載の方法。 6、排出ガス及び蒸気を220乃至250℃の温度で0
.5乃至100秒間加熱する特許請求の範囲第5項に記
載の方法。 7、テトラニトロメタン含有留分が68%以上の濃度の
硝酸からなる特許請求の範囲第1項に記載の方法。 8、硝酸を220乃至250℃の温度で0.5乃至10
0秒間加熱する特許請求の範囲第7項に記載の方法。
[Claims] 1. In a method for decomposing tetranitromethane produced as a by-product in a method of treating an organic substance with nitric acid, a tetranitromethane-containing fraction is heat-treated at a temperature of at least 210°C to decompose tetranitromethane. A method for decomposing tetranitromethane, characterized by: 2. Heat the tetranitromethane-containing fraction to 210 to 300°C.
The method according to claim 1, wherein the method is heated at a temperature of 0.1 to 200 seconds. 3. The method according to claim 1, wherein the method of treatment with nitric acid is nitration. 4. The method according to claim 1, wherein the method of treatment with nitric acid is oxidation. 5. The method according to claim 1, wherein the tetranitromethane-containing fraction consists of exhaust gas and steam. 6. Exhaust gas and steam at a temperature of 220 to 250℃
.. The method according to claim 5, wherein the heating is performed for 5 to 100 seconds. 7. The method according to claim 1, wherein the tetranitromethane-containing fraction comprises nitric acid with a concentration of 68% or more. 8. Add nitric acid to 0.5 to 10% at a temperature of 220 to 250°C.
The method according to claim 7, wherein the heating is performed for 0 seconds.
JP62083134A 1986-04-09 1987-04-06 Decomposition of tetranitromethane Pending JPS62244425A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CA000506238A CA1242459A (en) 1986-04-09 1986-04-09 Process for the destruction of by-product tetranitromethane
CA506238 1986-04-09

Publications (1)

Publication Number Publication Date
JPS62244425A true JPS62244425A (en) 1987-10-24

Family

ID=4132845

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62083134A Pending JPS62244425A (en) 1986-04-09 1987-04-06 Decomposition of tetranitromethane

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US (1) US4713232A (en)
EP (1) EP0241194B1 (en)
JP (1) JPS62244425A (en)
KR (1) KR890003833B1 (en)
CN (1) CN1009072B (en)
AT (1) ATE45886T1 (en)
AU (1) AU583452B2 (en)
CA (1) CA1242459A (en)
DE (1) DE3760490D1 (en)
ES (1) ES2011048B3 (en)
FI (1) FI871354A (en)
NO (1) NO871473L (en)
NZ (1) NZ219625A (en)
PT (1) PT84636B (en)
ZA (1) ZA872182B (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3813184A1 (en) * 1988-04-20 1989-11-02 Dynamit Nobel Ag METHOD FOR THE DECOMPOSITION OF EXPLOSIVE HYDROCHLORIC ACID ESTERS
US5589037A (en) * 1995-10-24 1996-12-31 General Electric Company Method for removing tetranitromethane from nitric acid
US5847240A (en) * 1997-03-24 1998-12-08 Arco Chemical Technology, L.P. Process for reducing tetranitromethane in compositions containing nitroaromatic compounds
WO1997038967A1 (en) * 1996-04-16 1997-10-23 Arco Chemical Technology, L.P. Reducing tetranitromethane in compositions containing nitroaromatic compounds
US6414143B1 (en) 1999-02-24 2002-07-02 Alliant Techsystems Inc. Extraction and recovery of nitramines from propellants, explosives, and pyrotechnics
US6416601B1 (en) 2000-03-10 2002-07-09 Alliant Techsystems Inc. Method of recovery for nitramines from aluminized energetic materials
US6610156B2 (en) 2000-03-10 2003-08-26 Alliant Techsystems Inc. Method for recovery of nitramines from aluminized energetic materials

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US1632959A (en) * 1923-12-31 1927-06-21 Gartner Richard Hans Method for removing tetranitromethane from trinitrotoluene
US2366309A (en) * 1941-04-17 1945-01-02 Du Pont Apparatus for the treatment of waste acid
US3781374A (en) * 1972-08-03 1973-12-25 Nitro Nobel Ab Method for the isolation of tetranitromethane from a solution of nitric acid with comparatively low contents of tetranitromethane
US4003977A (en) * 1975-08-18 1977-01-18 The United States Of America As Represented By The Secretary Of The Navy Removal of tetranitromethane from TNT plant waste gases
US4001373A (en) * 1975-08-18 1977-01-04 The United States Of America As Represented By The Secretary Of The Navy Removal of tetranitromethane from tnt plant waste

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DE3760490D1 (en) 1989-10-05
KR890003833B1 (en) 1989-10-05
PT84636B (en) 1989-05-12
AU583452B2 (en) 1989-04-27
NO871473D0 (en) 1987-04-08
CN1009072B (en) 1990-08-08
PT84636A (en) 1987-05-01
ATE45886T1 (en) 1989-09-15
AU7009787A (en) 1987-10-15
EP0241194B1 (en) 1989-08-30
ES2011048B3 (en) 1989-12-16
KR870009976A (en) 1987-11-30
FI871354A (en) 1987-10-10
NO871473L (en) 1987-10-12
EP0241194A1 (en) 1987-10-14
FI871354A0 (en) 1987-03-27
ZA872182B (en) 1987-11-25
NZ219625A (en) 1989-03-29
US4713232A (en) 1987-12-15
CN87102764A (en) 1987-11-18

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